Global Change Biology · 2007 · 157 citations · 23 references
AgricultureEarth SciencesSoil SciencesSoil FertilitySoil Organic MatterSoil ScienceGrazing Impacts On SoilNutrient Cycling In PasturesSoil Carbon LossesSoil Fertility DynamicsSoil HorizonsSoil Sampling StrategiesC HorizonsLand Use Change Effects On Soil Carbon LossPasture Nutrient RetentionSoil Carbon StocksSoil Organic CarbonSoil Organic Carbon LossSoil Organic Carbon Stocks LossSoil Profile Sampling
Abstract The conversion of two‐thirds of New Zealand's native forests and grasslands to agriculture has followed trends in other developed nations, except that pastoral grazing rather than cropping dominates agriculture. The initial conversion of land to pasture decreased soil acidity and elevated N and P stocks, but caused little change in soil organic C stocks. However, less is known about C and nutrient stock changes during the last two decades under long‐term pastoral management. We resampled 31 whole soil profiles in pastures spanning seven soil orders with a latitudinal range of 36–46°S, which had originally been sampled 17–30 years ago. We measured total C, total N, and bulk density for each horizon (generally to 1 m) and also reanalyzed archived soil samples of the same horizons for C and N. On average, profiles had lost significant amounts of C (− 2.1 kg C m −2 ) and N (− 0.18 kg N m −2 ) since initial sampling. Assuming a continuous linear decline in organic matter between sampling dates, significant losses averaged 106 g C m −2 yr −1 ( P =0.01) and 9.1 g N m −2 yr −1 ( P =0.002). Removal of C through leaching and erosion appears too small to explain these losses, suggesting losses from respiration exceed the inputs of photosynthate in the soil profile. These results emphasize that resampling soil profiles provide a robust method for detecting soil C changes, and add credence to the suggestion that soil C losses may be occurring in some temperate soil profiles. Further work is required to determine whether these losses are continuing and how losses might be extrapolated across landscapes to determine the implications for New Zealand's national CO 2 emissions and the sustainability of the implied rates of soil N loss.
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